# Loading packages and data
library(ggplot2)
library(ecodata)
library(lubridate)
library(dplyr)
library(stringr)
library(marmap) # bathymetry
library(RColorBrewer)
library(ggnewscale)
library(sf)
library(cowplot)
library(tidyverse)
library(ggpubr)
library(sf)
library(ggdist)
library(ggpubr)
library(wesanderson)
library(raster)
#library(glmTMB)
library(ggpmisc)
library(mgcViz)
library(gratia)
# CPUE data (no env covariates)
gt_data_model_cpue <- read.csv(here::here('data/catch_data/gt_data_model_cpue.csv'))
#names(gt_data_model_cpue) <- tolower(names(gt_data_model_cpue))
# Add in column with cpue
# note: Paul indicated to use small mesh
gt_data_model_cpue <- gt_data_model_cpue %>%
rename_all(., .funs = tolower) %>%
mutate(mesh_bin = case_when(mesh_size <= 5.6 ~ 'SM',mesh_size >= 5.6 ~ 'LG',
TRUE ~ 'NA')) %>%
mutate(cpue_hr = sum_gt_catch/effort_dur)
# Catch data:
sfobs <-readRDS(here::here('data/catch_data/gold_tile_sf_ob_v1_temp_price.rds'))
sfob.env <- sfobs %>%
mutate(mesh_bin = case_when(mesh_size <= 5.6 ~ 'SM', mesh_size >= 5.6 ~ 'LG',
TRUE ~ 'NA'),
cpue_hr = SUM_GT_CATCH/effort_dur) %>%
filter(YEAR %in% c(1998:2022) & mesh_bin == 'SM') %>%
dplyr::select(DATE, YEAR, MONTH, YDAY,trip_id,hull_num, area, effort_dur,
SUM_GT_CATCH, cpue_hr, mesh_size, mesh_bin, depth, start_lat, start_lon,
bottomT, bottomT_avg, MIN_TEMP_C, MEAN_TEMP_C, MAX_TEMP_C,
TEMP_VARIANCE, TEMP_DEVIATION, MEAN_DPTH_M, tri, sed) %>%
mutate(YEAR = as.integer(YEAR)) %>%
rename_all(., .funs = tolower)
areas <- sort(unique(sfob.env$area))
catch.tally.ann <- sfob.env %>% # aggregate by year
group_by(year) %>%
summarise(ttl_sum = sum(sum_gt_catch))
# Length data from observer program
lengths <- read.csv(here::here('data/catch_data/gt_data_length_andy.csv'))
names(lengths) <- tolower(names(lengths))
# Recruitment estimates from 2021 report
recruit <- read.csv(here::here('data/assessment_data/tilefish_rec_estimate_2021.csv'))
# Merge SF/Obs catch data with recruit estimates:
catch_recruit <- cbind(recruit %>% filter(year %in% c(1998:2020)),
catch.tally.ann %>%
filter(year %in% c(1998:2020)) %>%
dplyr::select(ttl_sum))
# loading in shape files for maps
US.areas <- st_read(here::here('shapefiles/USA.shp'), quiet = TRUE)
canada.areas <- st_read(here::here('shapefiles/Canada.shp'), quiet = TRUE)
bts_strata <- st_read(here::here('shapefiles/NES_BOTTOM_TRAWL_STRATA.shp'),
quiet = TRUE)
# plot(bts_strata) # to see all bottom trawl strata
gtf_strata <- bts_strata %>%
filter(STRATUMA %in% c('01030', '01040', '01070', '01080', '01110', '01120',
'01140', '01150', '01670', '01680', '01710', '01720',
'01750', '01760')) # select just the gtf strata
# plot(gtf_strata)
bathy <- marmap::getNOAA.bathy(-81,-58, 27, 46)
bathy = fortify.bathy(bathy)
Year-class strength is broadly defined as the number of fish spawned or hatched in a given year (Ricker, 1975).
Figure 1. Sum of catch (not accounting for effort), across years. Light blue shaded region represents the temporal range of observer records and red shaded region represents temporal range of study fleet records. The ‘purple’ region is where they overlap. Note that 2000-2005 for observer records had low sample size/number of vessels for tilefish, making the shaded region likely the best region to use for analysis. The vertical dashed lines represent strong year classes for this species (Nesslage et al. 2021). Red asterisk marks year that stock was deemed ‘re-built’.
# tot_catch == total (sum_catch) across hauls. so if tallying up annually,
# use sum_catch
# Strong year-classes: 1970, 1973, 1993, 1999, 2005, 2013
ggplot(catch.tally.ann, aes(x = factor(year), y = ttl_sum, group = 1))+
geom_rect(aes(xmin = '2007', xmax = '2022', ymin = -Inf, ymax = Inf),
fill = 'red', alpha = 0.02) +
geom_rect(aes(xmin = '2000', xmax = '2022', ymin = -Inf, ymax = Inf),
fill = 'lightblue', alpha = 0.05) +
geom_vline(xintercept = c('1993','1999', '2005', '2013'), lty = 2) +
geom_line(color = 'black', size = 1.5) +
annotate("text", label = "*",
x = 26, y = 14000, size = 8, colour = "red" )+
xlab('Year') +
ylab('Total sum tilefish catch') +
# facet_wrap(~month)+
theme(axis.text.x = element_text(color = 'black',
size = 12, angle = 45, vjust = 1, hjust=1)) +
ecodata::theme_facet()
Figure 2. Catch-per-unit-effot for undirected trawl trips from the Study fleet and observer program. Zeros have been added using species association methodology (via jaccard index).
gt_data_model_cpue %>%
filter(mesh_bin == 'SM') %>% # note: Paul indicated to use small mesh
group_by(year, source) %>%
summarise(mean_cpue = mean(cpue_hr),.groups = 'drop') %>%
ggplot(aes(x=year,y=mean_cpue)) +
geom_line(lwd = 1) +
facet_wrap(~source) +
theme_bw()
gt_data_model_cpue %>%
filter(mesh_bin == 'SM') %>%
group_by(year) %>%
summarise(mean_cpue = mean(cpue_hr),.groups = 'drop') %>%
ggplot(aes(x=year,y=mean_cpue)) +
geom_line(lwd = 1) +
labs(title = 'Study fleet + Observer combined') +
theme_bw()
Tilefish catch locations (study fleet/observer)
yrs = sort(unique(gt_data_model_cpue$year))
#for(i in 1:length(yrs)){
yrmap <- function(yrs){
gt_data_model_cpue %>%
filter(start_lat < 42.5 & depth_est > 50 & year == yrs) %>%
mutate(bin = cut(year, seq(min(year), max(year) + 4, 4), right = FALSE)) %>%
ggplot() +
geom_sf(data = US.areas %>% st_as_sf(),color = 'gray20', fill = '#cbdbcd') +
geom_contour(data = bathy,
aes(x=x,y=y,z=-1*z),
breaks=c(50,100,150,200, Inf),
size=c(0.3),
col = 'darkgrey') +
stat_summary_2d(aes(x=start_lon, y=start_lat, z = cpue_hr),
binwidth=c(0.16666,0.16666)) +
scale_fill_viridis_c() +
theme(legend.position = "bottom",
legend.key.size = unit(0.2, "cm"),
legend.key.width = unit(1, "cm")) +
coord_sf(xlim = c(-75,-65.5), ylim = c(36,44), datum = sf::st_crs(4326)) +
labs(x = '', y = '', fill = 'CPUE') +
theme_bw()
}
for(i in 1:length(yrs)){
cat("\n#####", as.character(yrs[i]),"\n")
print(yrmap(yrs[i]))
cat("\n")
}
Figure 3. Age-1 recruitment estimate from the 2021 tilefish assessment across all years
ggplot(recruit, aes(x = factor(year), y = recruit_est, group = 1))+
geom_rect(aes(xmin = '2007', xmax = '2022', ymin = -Inf, ymax = Inf),
fill = 'red', alpha = 0.02) +
geom_rect(aes(xmin = '2000', xmax = '2022', ymin = -Inf, ymax = Inf),
fill = 'lightblue', alpha = 0.05) +
geom_vline(xintercept = c('1993','1999', '2005', '2013'), lty = 2) +
geom_line(color = 'black', size = 1.5) +
annotate("text", label = "*",
x = 26, y = 14000, size = 8, colour = "red" )+
xlab('Year') +
ylab('Total sum tilefish catch') +
# facet_wrap(~month)+
theme(axis.text.x = element_text(color = 'black',
size = 12, angle = 45, vjust = 1, hjust=1)) +
ecodata::theme_facet()
### Thought: Should we isolate years associated w/strong year classes (or bad)
### for correlations and analyses?
Figure 4. Recruitment estimates in focus years
ggplot(recruit %>% filter(year %in% c(1998:2022)),
aes(x = factor(year), y = recruit_est, group = 1))+
geom_vline(xintercept = c('1993','1999', '2005', '2013'), lty = 2) +
geom_line(color = 'black', size = 1.2) +
xlab('Year') +
ylab('Recruit estimates') +
theme(axis.text.x = element_text(color = 'black',
size = 12, angle = 45, vjust = 1, hjust=1)) +
ecodata::theme_facet()
Figure 5. Recruitment estimates and Study Fleet and Observer catch data. Black line denotes recruitment estimate, yellow denotes sum of annual catch data across both Study fleet and Observer programs.
options(scipen=999)
ggplot(catch_recruit) +
geom_line(aes(x = factor(year), y = recruit_est, group = 1),
col = 'black', size = 1.2) +
geom_line(aes(x = factor(year), y = ttl_sum*1000), size = 1.2,
color = 'goldenrod1', group = 1) +
scale_y_continuous(sec.axis = sec_axis(~./1000, name = 'Catch (lbs)')) +
geom_vline(xintercept = c('1993','1999', '2005', '2013'), lty = 2) +
xlab('Year') +
ylab('Recruit estimates') +
theme(axis.text.x = element_text(color = 'black',
size = 12, angle = 45, vjust = 1, hjust=1)) +
ecodata::theme_facet()
Figure 6. Distribution of lengths Figure 7. Length frequencies Figure 8. Frequency of smaller individuals
# Define category breaks
size_breaks <- c(0,10,20,30,40, 50, 60, 70, 80, 90, 100)
# Making a function to bin the catches
label_interval <- function(breaks) {
paste0("(", breaks[1:length(breaks) - 1], "-", breaks[2:length(breaks)], ")")
}
labels = label_interval(size_breaks)
# length freq. table
tab = table(cut(lengths$lenanml,
breaks = size_breaks,
labels = label_interval(size_breaks)))
## Plot full distribution
ggplot(lengths,
aes(x = lenanml)) +
geom_bar(position = position_dodge(),
alpha = 0.4, fill= 'blue', color="black") +
xlab('Tilefish length (cm)') +
theme_bw() +
theme_facet()
# Plot length frequencies
barplot(tab, xlab = 'Length bins (mm)', main = '')
# Just the little ones
barplot(tab[1:3], xlab = 'Length bins (mm)', main = '')
Young of year - year 1 and 2 size class
ggplot(lengths %>% filter(lenanml <= 26),
aes(x = lenanml)) +
geom_bar(position = position_dodge(),
fill= 'slateblue', color="black") +
xlab('Tilefish length (cm)') +
theme_bw() +
theme_facet()
ggplot(lengths %>% filter(lenanml <= 26),
aes(x = lenanml, fill = numlen)) +
geom_bar(position = position_dodge(),
alpha = 0.4, fill= 'blue', color="black") +
xlab('Tilefish length (cm)') +
theme_bw() +
facet_wrap(~year) +
theme_facet()
The strong year classes for Golden Tilefish were 1993, 1998, 2005, 2013. Some of the underlying oceanographic processes that may be related to recruitment may influence habitat, retention/displacement and food availablity. These are explored below.
Tilefish occupy a very narrow band of habitat conditions. Therefore, temperature and salinity may be of interest.
# SST
Figure 1. GLORYS vs in-situ bottom temperatures from study fleet vessels.
Figure 2. Bottom temperature (C) across years. Blue dots are in-situ data, red dots are from GLORYS.
ggplot2::ggplot(sfob.env, aes(x=bottomt, y=mean_temp_c)) +
geom_point(color="blue", alpha=0.1)+
geom_abline(intercept = 0, slope = 1) +
xlab('Bottom Temp (SF)') +
ylab('Bottom Temp (GLORYS)') +
theme_bw()
ggplot2::ggplot(sfob.env, aes(x=bottomt, y=year)) +
geom_point(color="blue", alpha=0.1) +
geom_point(data = sfob.env, aes(x=mean_temp_c, y=year),
color="red", alpha=0.1) +
xlab('Bottom Temp') +
ylab('Year') +
labs(color = 'Source') +
theme_bw()
jet.colors <-colorRampPalette(c("blue", "#007FFF", "cyan","#7FFF7F", "yellow", "#FF7F00", "red", "#7F0000"))
# select just years with study fleet bottom temps
sf.bt <- sfob.env %>% filter(year>2006 & depth > 50)
yrs = sort(unique(sf.bt$year))
#for(i in 1:length(yrs)){
yrmap <- function(yrs){
sf.bt %>% filter(year == yrs) %>%
ggplot() +
geom_sf(data = US.areas %>% st_as_sf(),color = 'gray20', fill = '#cbdbcd') +
geom_contour(data = bathy,
aes(x=x,y=y,z=-1*z),
breaks=c(50,100,150,200, Inf),
size=c(0.3),
col = 'darkgrey') +
stat_summary_2d(aes(x=start_lon, y=start_lat, z = bottomt),
binwidth=c(0.16666,0.16666)) +
scale_fill_gradientn(colors = jet.colors(20)) +
coord_sf(xlim = c(-75,-65.5), ylim = c(36,44), datum = sf::st_crs(4326)) +
labs(x = '', y = '', fill = 'Bottom temperature (°C)') +
theme_bw()
}
for(i in 1:length(yrs)){
cat("\n######", as.character(yrs[i]),"\n")
print(yrmap(yrs[i]))
cat("\n")
}
The following figures compare in-situ bottom temperature from the study-fleet data set to the recruitment estimate.
# Note here temperatures are averaged across all depths > 50 for each month.
# Create in-situ bottom temps by month w/lag
df.lag = sfob.env %>% filter(year > 2006 & depth > 50) %>%
group_by(year,month) %>%
summarise(mean_dpth = mean(depth),
mean_bt = mean(bottomt)) %>%
mutate(mean_bt_lag2 = lag(mean_bt,2),
mean_bt_lag3 = lag(mean_bt,3),
mean_bt_lag6 = lag(mean_bt, 6))
# Join in-situ bottom temps w/assessment recruitment estimate
df.join = dplyr::full_join(recruit, df.lag, by = join_by(year)) %>%
dplyr::select(year, month, recruit_est, mean_dpth,
mean_bt, mean_bt_lag2, mean_bt_lag3, mean_bt_lag6) %>%
tidyr::drop_na()
# See what months have data
sort(unique(df.join$month))
## [1] 7 8 9 10 11 12
hist(df.join$month) # will group into spring/summer fall/winter categories
## spring/summer bottom temp no lag
ggplot2::ggplot(df.join %>% filter(month %in% c(4,5,6,7,8)),
aes(x=recruit_est, y=mean_bt)) +
geom_point(color = 'black') +
stat_smooth(method = "lm",
formula = y ~ x,
geom = "smooth") +
xlab('Recruitment estimate') +
ylab('Mean bottom temp (°C)')+
stat_cor(aes(label=..rr.label..)) +
theme_bw()
## spring/summer bottom temp no lag
ggplot2::ggplot(df.join %>% filter(month %in% c(9,10,11,12)),
aes(x=recruit_est, y=mean_bt)) +
geom_point(color= 'black')+
stat_smooth(method = "lm",
formula = y ~ x,
geom = "smooth") +
xlab('Recruitment estimate') +
ylab('Mean bottom temp (°C)')+
stat_cor(aes(label=..rr.label..)) +
theme_bw()
## spring/summer bottom temp 2 month lag
ggplot2::ggplot(df.join %>% filter(month %in% c(4,5,6,7,8)),
aes(x = recruit_est, y = mean_bt_lag2)) +
geom_point(color = 'black') +
stat_smooth(method = "lm",
formula = y ~ x,
geom = "smooth") +
xlab('Recruitment estimate') +
ylab('Mean bottom temp (°C)')+
labs(title = 'Lag 2 months') +
stat_cor(aes(label=..rr.label..)) +
theme_bw()
## spring/summer bottom temp 2 month lag
ggplot2::ggplot(df.join %>% filter(month %in% c(9,10,11,12)),
aes(x = recruit_est, y = mean_bt_lag2)) +
geom_point(color= 'black')+
stat_smooth(method = "lm",
formula = y ~ x,
geom = "smooth") +
xlab('Recruitment estimate') +
ylab('Mean bottom temp (°C)')+
labs(title = 'Lag 2 months') +
stat_cor(aes(label=..rr.label..)) +
theme_bw()
## spring/summer bottom temp 3 month lag
ggplot2::ggplot(df.join %>% filter(month %in% c(4,5,6,7,8)),
aes(x = recruit_est, y = mean_bt_lag3)) +
geom_point(color = 'black') +
stat_smooth(method = "lm",
formula = y ~ x,
geom = "smooth") +
xlab('Recruitment estimate') +
ylab('Mean bottom temp (°C)')+
labs(title = 'Lag 3 months') +
stat_cor(aes(label=..rr.label..)) +
theme_bw()
## spring/summer bottom temp 3 month lag
ggplot2::ggplot(df.join %>% filter(month %in% c(9,10,11,12)),
aes(x = recruit_est, y = mean_bt_lag3)) +
geom_point(color= 'black')+
stat_smooth(method = "lm",
formula = y ~ x,
geom = "smooth") +
xlab('Recruitment estimate') +
ylab('Mean bottom temp (°C)')+
labs(title = 'Lag 3 months') +
stat_cor(aes(label=..rr.label..)) +
theme_bw()
## spring/summer bottom temp 6 month lag
ggplot2::ggplot(df.join %>% filter(month %in% c(4,5,6,7,8)),
aes(x = recruit_est, y = mean_bt_lag6)) +
geom_point(color = 'black') +
stat_smooth(method = "lm",
formula = y ~ x,
geom = "smooth") +
xlab('Recruitment estimate') +
ylab('Mean bottom temp (°C)')+
labs(title = 'Lag 6 months') +
stat_cor(aes(label=..rr.label..)) +
theme_bw()
## spring/summer bottom temp 6 month lag
ggplot2::ggplot(df.join %>% filter(month %in% c(9,10,11,12)),
aes(x = recruit_est, y = mean_bt_lag6)) +
geom_point(color= 'black')+
stat_smooth(method = "lm",
formula = y ~ x,
geom = "smooth") +
xlab('Recruitment estimate') +
ylab('Mean bottom temp (°C)')+
labs(title = 'Lag 6 months') +
stat_cor(aes(label=..rr.label..)) +
theme_bw()
Here we explore salinity from the GLORYS reanalysis model at three different depths
# Salinity
jet.colors <-colorRampPalette(c("blue", "#007FFF", "cyan","#7FFF7F", "yellow", "#FF7F00", "red", "#7F0000"))
# b <- brick(here::here('data/salinity/dd_sal_55_2000_2009.tif'))
# b.00 <- b[,,,1:365]
# select just years with study fleet bottom temps
sf.bt <- sfob.env %>% filter(year>2006 & depth > 50)
yrs = sort(unique(sf.bt$year))
#for(i in 1:length(yrs)){
yrmap <- function(yrs){
sf.bt %>% filter(year == yrs) %>%
ggplot() +
geom_sf(data = US.areas %>% st_as_sf(),color = 'gray20', fill = '#cbdbcd') +
geom_contour(data = bathy,
aes(x=x,y=y,z=-1*z),
breaks=c(50,100,150,200, Inf),
size=c(0.3),
col = 'darkgrey') +
# stat_summary_2d(aes(x=start_lon, y=start_lat, z = bottomt),
# binwidth=c(0.16666,0.16666)) +
# scale_fill_gradientn(colors = jet.colors(20)) +
coord_sf(xlim = c(-75,-65.5), ylim = c(36,44), datum = sf::st_crs(4326)) +
labs(x = '', y = '', fill = 'Salinty') +
theme_bw()
}
for(i in 1:length(yrs)){
cat("\n######", as.character(yrs[i]),"\n")
print(yrmap(yrs[i]))
cat("\n")
}
Cross-shelf processes may influence the retention or displacement of tilefish during early life history stages. These are explored below.
Shelf water volume: A measure of the volume of water bounded inshore of the shelf-slope front. In this analysis, shelf water is defined as all water having salinity <34 psu. The position of the shelf-slope front varies inter-annually with the higher shelf water values indicating the front being pushed further towards the shelf break.
high shv: front pushed towards sbf low shv: front pushed inshore (more slope water on shelf)
Hypothesis: Higher recruitment success correlated with years of higher shelf water volume in spring/summer. These months months may be particularly important as that is when spawning is occurring and the position of the sbf may influence the position of larvae (away from spawning grounds).
Additional variables in this dataset are shelf water temperature and salinity which may also be indicative of habitat conditions.
# Shelf water volume
shlfvol <- read.csv(here::here('data/shelf_water_volume/ShelfWaterVolume_BSB_update.csv'))
# wrangling date info, converting doy to date and month
yrs <- as.vector(nrow(shlfvol))
shlfvol$Year <- as.character(shlfvol$Year)
for (i in 1:nrow(shlfvol)){
yrs[i] <- strsplit(shlfvol$Year, ".", fixed = TRUE)[[i]][1]
}
shlfvol$year <- yrs
shlfvol <- shlfvol %>% mutate(date_= as.Date(Year.Day-1,
origin=paste0(year, "-01-01")),
month= strftime(date_, "%m"),
day=strftime(date_,"%d"),
year = as.integer(year),
month = as.numeric(month))
# Create shw vol by month w/lag
df.lag = shlfvol %>%
group_by(year,month) %>%
summarise(mean_t = mean(ShW.T),
mean_s = mean(ShW.S),
mean_v = mean(ShW.Vol)) %>%
mutate(mean_t_lag2 = lag(mean_t,2),
mean_t_lag3 = lag(mean_t,3),
mean_t_lag6 = lag(mean_t,6),
mean_s_lag2 = lag(mean_s,2),
mean_s_lag3 = lag(mean_s,3),
mean_s_lag6 = lag(mean_s,6),
mean_v_lag2 = lag(mean_v,2),
mean_v_lag3 = lag(mean_v,3),
mean_v_lag6 = lag(mean_v,6))
# Join in-situ bottom temps w/assessment recruitment estimate
df.join = dplyr::full_join(recruit, df.lag, by = join_by(year)) %>%
dplyr::select(year, month, recruit_est, mean_t, mean_s, mean_v,
mean_t_lag2, mean_s_lag2, mean_v_lag2,
mean_t_lag3, mean_s_lag3, mean_v_lag3) %>%
tidyr::drop_na()
# See what months have data
sort(unique(df.join$month))
## [1] 7 8 9 10 11
hist(df.join$month) # will group into spring/summer fall/winter categories
## Shelf water volume no lag
ggplot2::ggplot(df.join,
aes(x=recruit_est, y=mean_v)) +
geom_point(color = 'black') +
stat_smooth(method = "lm",
formula = y ~ x,
geom = "smooth") +
xlab('Recruitment estimate') +
ylab('Mean shelf water volume') +
labs(title = 'Shelf water volume') +
stat_cor(aes(label=..rr.label..)) +
theme_bw()
## Shelf water temperature no lag
ggplot2::ggplot(df.join,
aes(x=recruit_est, y=mean_t)) +
geom_point(color = 'black') +
stat_smooth(method = "lm",
formula = y ~ x,
geom = "smooth") +
xlab('Recruitment estimate') +
ylab('Mean shelf water temperature') +
labs(title = 'Shelf water temperature') +
stat_cor(aes(label=..rr.label..)) +
theme_bw()
## Shelf water salinity no lag
ggplot2::ggplot(df.join,
aes(x=recruit_est, y=mean_s)) +
geom_point(color = 'black') +
stat_smooth(method = "lm",
formula = y ~ x,
geom = "smooth") +
xlab('Recruitment estimate') +
ylab('Mean shelf water salinity') +
labs(title = 'Shelf water salinity') +
stat_cor(aes(label=..rr.label..)) +
theme_bw()
ggplot2::ggplot(df.join %>% filter(year >1997 & month %in% c(7,8,9)),
aes(x=recruit_est, y=mean_s)) +
geom_point() +
geom_smooth(method = "lm", formula = y ~ x, size = 1, se = FALSE,
aes(colour = 'Linear')) +
geom_smooth(method = "lm", formula = y ~ x + I(x^2),
size = 1, se = FALSE, aes(colour = 'Quadratic')) +
geom_smooth(method = "loess", formula = y ~ x,
size = 1, se = FALSE, aes(colour = 'Loess')) +
geom_smooth(method = "gam", formula = y ~ s(x),
size = 1, se = FALSE, aes(colour = 'Gam')) +
geom_smooth(method = "gam", formula = y ~ s(x, k = 3),
size = 1, se = FALSE, aes(colour = 'Gam2')) +
labs(title = 'Recruitment est x M.S.W July,Aug,Sept (1998:2020)') +
scale_color_manual(name='Model',
breaks=c('Linear', 'Quadratic', 'Loess', 'Gam', 'Gam2'),
values=c('Linear'='black', 'Quadratic'='blue',
'Loess'='red', 'Gam' = 'green',
'Gam2' = 'purple')) +
theme_bw()
With lags
2 Months
## Shelf water volume 2 month lag
ggplot2::ggplot(df.join,
aes(x=recruit_est, y=mean_v_lag2)) +
geom_point(color = 'black') +
stat_smooth(method = "lm",
formula = y ~ x,
geom = "smooth") +
xlab('Recruitment estimate') +
ylab('Mean shelf water volume') +
labs(title = 'Shelf water volume - lag 2 months') +
stat_cor(aes(label=..rr.label..)) +
theme_bw()
## Shelf water temperature 2 month lag
ggplot2::ggplot(df.join,
aes(x=recruit_est, y=mean_t_lag2)) +
geom_point(color = 'black') +
stat_smooth(method = "lm",
formula = y ~ x,
geom = "smooth") +
xlab('Recruitment estimate') +
ylab('Mean shelf water temperature') +
labs(title = 'Shelf water temperature - lag 2 months') +
stat_cor(aes(label=..rr.label..)) +
theme_bw()
## Shelf water salinity 2 month lag
ggplot2::ggplot(df.join,
aes(x=recruit_est, y=mean_s_lag2)) +
geom_point(color = 'black') +
stat_smooth(method = "lm",
formula = y ~ x,
geom = "smooth") +
xlab('Recruitment estimate') +
ylab('Mean shelf water salinity') +
labs(title = 'Shelf water salinity - lag 2 months') +
stat_cor(aes(label=..rr.label..)) +
theme_bw()
3 Months
## Shelf water volume 3 month lag
ggplot2::ggplot(df.join,
aes(x=recruit_est, y=mean_v_lag3)) +
geom_point(color = 'black') +
stat_smooth(method = "lm",
formula = y ~ x,
geom = "smooth") +
xlab('Recruitment estimate') +
ylab('Mean shelf water volume') +
labs(title = 'Shelf water volume - lag 3 months') +
stat_cor(aes(label=..rr.label..)) +
theme_bw()
## Shelf water temperature 3 month lag
ggplot2::ggplot(df.join,
aes(x=recruit_est, y=mean_t_lag3)) +
geom_point(color = 'black') +
stat_smooth(method = "lm",
formula = y ~ x,
geom = "smooth") +
xlab('Recruitment estimate') +
ylab('Mean shelf water temperature') +
labs(title = 'Shelf water temperature - lag 3 months') +
stat_cor(aes(label=..rr.label..)) +
theme_bw()
## Shelf water salinity 3 month lag
ggplot2::ggplot(df.join,
aes(x=recruit_est, y=mean_s_lag3)) +
geom_point(color = 'black') +
stat_smooth(method = "lm",
formula = y ~ x,
geom = "smooth") +
xlab('Recruitment estimate') +
ylab('Mean shelf water salinity') +
labs(title = 'Shelf water salinity - lag 3 months') +
stat_cor(aes(label=..rr.label..)) +
theme_bw()
Annual
# Create shw vol by year w/lag
df.lag = shlfvol %>%
group_by(year) %>%
summarise(mean_t = mean(ShW.T),
mean_s = mean(ShW.S),
mean_v = mean(ShW.Vol)) %>%
mutate(mean_t_lag2 = lag(mean_t,2),
mean_t_lag3 = lag(mean_t,3),
mean_t_lag6 = lag(mean_t,6),
mean_s_lag2 = lag(mean_s,2),
mean_s_lag3 = lag(mean_s,3),
mean_s_lag6 = lag(mean_s,6),
mean_v_lag2 = lag(mean_v,2),
mean_v_lag3 = lag(mean_v,3),
mean_v_lag6 = lag(mean_v,6))
# Join in-situ bottom temps w/assessment recruitment estimate
df.join = dplyr::full_join(recruit, df.lag, by = join_by(year)) %>%
dplyr::select(year,recruit_est, mean_t, mean_s, mean_v,
mean_t_lag2, mean_s_lag2, mean_v_lag2,
mean_t_lag3, mean_s_lag3, mean_v_lag3,
mean_t_lag6, mean_s_lag6, mean_v_lag6) %>%
tidyr::drop_na()
## Shelf water vol
ggplot2::ggplot(df.join,
aes(x=year, y=mean_v)) +
geom_point(color = 'black') +
geom_line(color = 'black') +
xlab('Year') +
ylab('Mean shelf water volume') +
labs(title = 'Shelf water volume') +
theme_bw()
ggplot2::ggplot() +
geom_line(data = df.join, aes(x=year, y=mean_s), color = 'red') +
geom_line(data = df.join,aes(x=year, y=mean_t*1), color = 'blue') +
ylim(30.0,34.0) +
scale_y_continuous(name = 'Sh.Water Salinity',
sec.axis = sec_axis(~./1, name = 'Sh.Water Temperature')) +
xlab('Year') +
labs(title = 'Shelf water salinity/temperature') +
theme_bw()
ggplot2::ggplot() +
geom_line(data = df.join, aes(x=year, y=mean_s), color = 'red') +
xlab('Year') +
ylab('Mean shelf water salinity') +
labs(title = 'Shelf water salinity') +
theme_bw()
## Shelf water vol no lag
ggplot2::ggplot(df.join,
aes(x=recruit_est, y=mean_v)) +
geom_point(color = 'black') +
stat_smooth(method = "lm",
formula = y ~ x,
geom = "smooth") +
xlab('Recruitment estimate') +
ylab('Mean shelf water volume') +
labs(title = 'Shelf water volume') +
stat_cor(aes(label=..rr.label..)) +
theme_bw()
## Shelf water temperature no lag
ggplot2::ggplot(df.join,
aes(x=recruit_est, y=mean_t)) +
geom_point(color = 'black') +
stat_smooth(method = "lm",
formula = y ~ x,
geom = "smooth") +
xlab('Recruitment estimate') +
ylab('Mean shelf water temperature') +
labs(title = 'Shelf water temperature') +
stat_cor(aes(label=..rr.label..)) +
theme_bw()
## Shelf water salinity no lag
ggplot2::ggplot(df.join,
aes(x=recruit_est, y=mean_s)) +
geom_point(color = 'black') +
stat_smooth(method = "lm",
formula = y ~ x,
geom = "smooth") +
xlab('Recruitment estimate') +
ylab('Mean shelf water salinity') +
labs(title = 'Shelf water salinity') +
stat_cor(aes(label=..rr.label..)) +
theme_bw()
With lags
## Shelf water vol 6 yr lag
ggplot2::ggplot(df.join,
aes(x=recruit_est, y=mean_v_lag6)) +
geom_point(color = 'black') +
stat_smooth(method = "lm",
formula = y ~ x,
geom = "smooth") +
xlab('Recruitment estimate') +
ylab('Mean shelf water volume') +
labs(title = 'Shelf water volume - lag 6 years') +
stat_cor(aes(label=..rr.label..)) +
theme_bw()
## Shelf water temperature 6 yr lag
ggplot2::ggplot(df.join,
aes(x=recruit_est, y=mean_t_lag6)) +
geom_point(color = 'black') +
stat_smooth(method = "lm",
formula = y ~ x,
geom = "smooth") +
xlab('Recruitment estimate') +
ylab('Mean shelf water temperature') +
labs(title = 'Shelf water temperature - lag 6 years') +
stat_cor(aes(label=..rr.label..)) +
theme_bw()
## Shelf water salinity 6 yr lag
ggplot2::ggplot(df.join,
aes(x=recruit_est, y=mean_s_lag6)) +
geom_point(color = 'black') +
stat_smooth(method = "lm",
formula = y ~ x,
geom = "smooth") +
xlab('Recruitment estimate') +
ylab('Mean shelf water salinity') +
labs(title = 'Shelf water salinity - lag 6 years') +
stat_cor(aes(label=..rr.label..)) +
theme_bw()
print(paste0('correlation: ', round(cor(df.join[,2], df.join[,13]), 4)))
## [1] "correlation: 0.2489"
Gulf stream index was calculated based on method presented by Pérez-Hernández and Joyce (2014). The gulf stream index (GSI) is a measure of the degrees latitude above the average Gulf Stream position based on ocean temperature at 200m (15 C) depth between 55W to 75W.
Positive values indicate a the mean position of the GS is more Northernly, whereas negative values indicate a more Southernly position.
# positive are more Northerly, negative are more southernly
## --- Note below is the original data source, which was modified to include
## --- month and then saved as a new file (mm_gsi_1954_2022_chen.csv).
# gsi.a <- ecodata::gsi
# gsi.m <- read.csv(here::here('data/gulf_stream_index/Chen_EN4_T200_GSI_1954_2022_monthly - Zhuomin Chen.xlsx - Sheet1.csv'))
# # weird inefficient solution I came up with to get month values (but it works)
# gsi.m$year <- as.numeric(gsub("(^\\d{4}).*", "\\1", gsi.m$Month))
# gsi.m$m.1 <- round(str_extract(gsi.m$Month, '\\d+([.,]\\d+)?') %>% as.numeric()- gsi.m$year,2)
# gsi.m$month <- round(as.numeric(str_extract(gsi.m$m.1, '\\d\\d')))
# is.na(gsi.m$month) <- 10
# gsi.m$month <- replace(gsi.m$month, is.na(gsi.m$month), 10)
# gsi.m <- gsi.m[,-4]
# # saving so don't have to do that everytime:
# write.csv(gsi.m, 'mm_gsi_1954_2022_chen.csv') #
gsi.m <- read.csv(here::here('data/gulf_stream_index/mm_gsi_1954_2022_chen.csv'))
# df <- dplyr::full_join(recruit, gsi.m, by = join_by(year)) %>%
# dplyr::select(year, month, recruit_est, GSI) %>%
# filter(month %in% c(3:9)) %>%
# tidyr::pivot_wider(names_from = c(month),
# values_from = c(GSI)) %>%
# rlang::set_names(c('year','recruit_est','Mar', 'Apr', 'May', 'Jun', 'Jul', 'Aug', 'Sep')) %>%
# tidyr::drop_na()
## --- This joins recruit estimate data to GSI data and
## --- calculates some summary stats(mean, sd, min, max)
df <- dplyr::full_join(recruit, gsi.m %>%
group_by(year) %>%
filter(month %in% c(3:8)) %>%
summarise(m.gsi = mean(GSI),
sd.gsi = sd(GSI),
max.gsi = max(GSI),
min.gsi = min(GSI)),
by = join_by(year)) %>%
mutate(pos = ifelse(m.gsi > 0, 'Northerly', 'Southerly'),
n.pos = ifelse(m.gsi > 0, 1, 0))
df <- df[-c(51:69),] # this removes rows w/years that don't match
# (could/should do this before hand in more standardized way - will do later)
# Plot the time series (mean GSI for the months of interest)
# -- Note: here I am looking just at March through August assuming these
# months are the most important to recently spawned individuals
ggplot(data = df,
aes(x = year, y = m.gsi)) +
geom_line(lwd = 1) +
geom_hline(yintercept = 0, lty = 2) +
labs(title = 'Mean GS position anomaly March:August',
x = 'Year',
y = "Gulf stream position anomaly\n") +
theme_bw()
# dplyr::full_join(recruit, gsi.m, by = join_by(year)) %>%
# dplyr::select(year, month, recruit_est, GSI) %>%
# #filter(month %in% c(3:9)) %>%
# filter(year>1997) %>%
# tidyr::drop_na() %>%
# ggplot2::ggplot(.,aes(x=recruit_est, y=GSI)) +
# geom_point(color = 'black') +
# xlab('Recruitment estimate') +
# ylab('Gulf stream position anomaly') +
# labs(title = 'Gulf stream index') +
# geom_hline(yintercept = 0, lty = 2) +
# theme_bw()
# Looking across all months
dplyr::full_join(recruit, gsi.m, by = join_by(year)) %>%
dplyr::select(year, month, recruit_est, GSI) %>%
#filter(month %in% c(3:9)) %>%
filter(year>1997) %>%
tidyr::drop_na() %>%
ggplot2::ggplot(.,aes(x=recruit_est, y=GSI)) +
geom_point(color = 'black') +
facet_wrap(~month)+
xlab('Recruitment estimate') +
ylab('Gulf stream position anomaly') +
labs(title = 'Gulf stream index by month') +
geom_hline(yintercept = 0, lty = 2) +
theme_bw()
# Looking across April through July
dplyr::full_join(recruit, gsi.m, by = join_by(year)) %>%
dplyr::select(year, month, recruit_est, GSI) %>%
#filter(month %in% c(3:9)) %>%
filter(year>1997 & month %in% c(4:7)) %>%
tidyr::drop_na() %>%
ggplot2::ggplot(.,aes(x=recruit_est, y=GSI)) +
geom_point(color = 'black') +
xlab('Recruitment estimate') +
ylab('Gulf stream position anomaly') +
labs(title = 'Gulf stream index (Apr:Jul)') +
geom_hline(yintercept = 0, lty = 2) +
theme_bw()
df.cor = dplyr::full_join(recruit, gsi.m, by = join_by(year)) %>%
dplyr::select(year, month, recruit_est, GSI) %>%
#filter(month %in% c(3:9)) %>%
filter(year>1997 & month %in% c(4:7)) %>%
tidyr::drop_na()
print(paste0('correlation: ', round(cor(df.cor[,3], df.cor[,4]), 4)))
## [1] "correlation: 0.1149"
Should I add a lag? If so, how much? From Nesslage_ea_21: For the Northern stock- From the original 49 explanatory variables, the final RF model included 10 variables: annual AMO (lagged 5–7 years); December to April AMO (lagged 5–7 years); station-based December to February NAO (lagged 3 and 4 years); PC-based December to February NAO (lagged 4 years), and management time block (Table 1; Figure S3). The final GAMM based on backward selection of variables in- cluded December to April AMO lagged 7 years and station-based December to February NAO lagged 3 and 4 years (Table 1). The shapes of the relationships approximated by the RF and GAMM indi- cate that golden tilefish landings were higher during negative AMO and positive NAO, with their respective lags (Figures 2 and 3). The largest range of the smoothed term on the y-axis corresponded with December to April AMO lagged 7 years (Figures 2 and 3) and this co- variate contributed 52.5% of the GAM R2 (Figure 4), implying AMO has the largest influence on northern landings. In contrast, NAO co-variates at lags of 3 and 4 years contributed a combined 47.5% of the GAM R2 (Figure 4).
The random forest using the full dataset identified 62 significant variables from the original 121 explanatory variables (Table 1), including two versions of the AMO (annual and seasonal with each lagged 0–7 years), both seasonal versions of PC-based NAO (each lagged 0–7 years), Labrador Current transport indices (NE Track 191: lagged 0, 4, 9, and 10 quarters), Gulf Stream index of position anomalies (lagged 0, 1, 4–10, and 12 quarters), Gulf stream position indices (lagged 0–3 years), Gulf stream transport index (lagged 0–3 years), bottom temperature anomalies (lagged 0–2, 4–7 years), and time block (Figure S1). The final GAMM for northern CPUE in- cluded four variables: annual AMO lagged 6 years, December to April AMO lagged 7 years, Gulf Stream index of position anomalies lagged 12 quarters, and the Labrador Current transport index for NE Track 191 unlagged (Table 1; Figure 5). Annual AMO lagged 6 years and December to April AMO lagged 7 years contributed a combined 64.1% of the GAM R2(Figure 4). Gulf Stream and Labrador Current transport indices contributed only 19.7% and 16.2%, respectively, of the GAM R2(Figure 4).
# recruitment index across all years
dplyr::full_join(recruit, gsi.m %>%
group_by(year) %>%
filter(month %in% c(3:8)) %>%
summarise(m.gsi = mean(GSI)),
by = join_by(year)) %>%
ggplot2::ggplot(., aes(x=recruit_est, y=m.gsi)) +
geom_point(color = 'black') +
geom_hline(yintercept = 0, lty = 2)+
labs(title = 'All years') +
xlab('Recruitment estimate') +
ylab('Gulf stream position anomaly') +
geom_smooth(method = "lm", formula = y ~ x, size = 1, se = FALSE,
aes(colour = 'Linear')) +
geom_smooth(method = "lm", formula = y ~ x + I(x^2),
size = 1, se = FALSE, aes(colour = 'Quadratic')) +
geom_smooth(method = "loess", formula = y ~ x,
size = 1, se = FALSE, aes(colour = 'Loess')) +
geom_smooth(method = "gam", formula = y ~ s(x),
size = 1, se = FALSE, aes(colour = 'Gam')) +
geom_smooth(method = "gam", formula = y ~ s(x, k = 3),
size = 1, se = FALSE, aes(colour = 'Gam2')) +
scale_color_manual(name='Model',
breaks=c('Linear', 'Quadratic', 'Loess', 'Gam', 'Gam2'),
values=c('Linear'='black', 'Quadratic'='blue',
'Loess'='red', 'Gam' = 'green',
'Gam2' = 'purple')) +
theme_bw()
# recruitment index across just the years that Paul recommended + el nino 1998
tt = dplyr::full_join(recruit, gsi.m %>%
group_by(year) %>%
filter(month %in% c(3:8)) %>%
summarise(m.gsi = mean(GSI)),
by = join_by(year))
ggplot2::ggplot(tt %>% filter(year>1997), aes(x=recruit_est, y=m.gsi)) +
geom_point(color = 'black') +
geom_hline(yintercept = 0, lty = 2)+
labs(title = '1998:2020, No outliers') +
xlab('Recruitment estimate') +
ylab('Gulf stream position anomaly') +
geom_smooth(method = "lm", formula = y ~ x, size = 1, se = FALSE,
aes(colour = 'Linear')) +
geom_smooth(method = "lm", formula = y ~ x + I(x^2),
size = 1, se = FALSE, aes(colour = 'Quadratic')) +
geom_smooth(method = "loess", formula = y ~ x,
size = 1, se = FALSE, aes(colour = 'Loess')) +
geom_smooth(method = "gam", formula = y ~ s(x),
size = 1, se = FALSE, aes(colour = 'Gam')) +
geom_smooth(method = "gam", formula = y ~ s(x, k = 3),
size = 1, se = FALSE, aes(colour = 'Gam2')) +
scale_color_manual(name='Model',
breaks=c('Linear', 'Quadratic', 'Loess', 'Gam', 'Gam2'),
values=c('Linear'='black', 'Quadratic'='blue',
'Loess'='red', 'Gam' = 'green',
'Gam2' = 'purple')) +
theme_bw()
ggplot(data = df, # add the data
aes(x = year, y = m.gsi, # set x, y coordinates
color = pos)) + # color by GS position
geom_boxplot() +
facet_grid(~pos) + # create panes base on GS position
ecodata::theme_facet()
# this gives main effects AND interactions
pos_aov <- aov(recruit_est ~ year * pos,
data = df)
# look at effects and interactions
# summary(pos_aov)
tidy_pos_aov <- broom::tidy(pos_aov)
tidy_pos_aov
## # A tibble: 4 × 6
## term df sumsq meansq statistic p.value
## <chr> <dbl> <dbl> <dbl> <dbl> <dbl>
## 1 year 1 3.85e11 384693730334. 0.717 0.401
## 2 pos 1 5.37e10 53734167452. 0.100 0.753
## 3 year:pos 1 6.82e11 682304704182. 1.27 0.265
## 4 Residuals 46 2.47e13 536176435236. NA NA
# write.csv(tidy_pos_aov, 'gs_pos_aov.csv')
ggplot(data = df,
aes(x = recruit_est/1000, y = m.gsi, fill = pos,
group = year)) +
geom_bar(color = "black", stat = "identity",
position = position_dodge2(preserve = "single"), width = 20) +
theme_bw() +
labs(title = 'All years',
x = "\nRecruitment estimate (x1000)",
y = "Gulf stream position anomaly\n")
ggplot(data = df %>% filter(year <= 1999),
aes(x = recruit_est/1000, y = m.gsi, fill = pos,
group = year)) +
geom_bar(color = "black", stat = "identity",
position = position_dodge2(preserve = "single"), width = 40) +
theme_bw() +
labs(title = '1971:1999',
x = "\nRecruitment estimate (x1000)",
y = "Gulf stream position anomaly\n")
ggplot(data = df %>% filter(year >1999),
aes(x = recruit_est/1000, y = m.gsi, fill = pos,
group = year)) +
geom_bar(color = "black", stat = "identity",
position = position_dodge2(preserve = "single"), width = 40) +
theme_bw() +
labs(title = '2000:2020',
x = "\nRecruitment estimate (x1000)",
y = "Gulf stream position anomaly\n")
Larval tilefish eat zooplankton, likely calanus. Calanus finmarchicus are a copepod (crustacean) with a one-year life cycle and are an important food source for many commercially important species. Calanus spp. are lipid rich, herbivorous species that eat phytoplankton, diatoms in particular (Hobbs et al. 2020).
Diatoms are often represented as microplankton (>20 µm), but many species are of the nanoplankton size class (2-20 µm), and a smaller few may even overlap with picoplanton size class (<2 µm).
Calanus is not as common in MAB, need to figure out dominant zooplankton in MAB.
# Calanus
calanus <- ecodata::calanus_stage %>% filter(Time %in% c(1998:2021))%>%
rename_all(., .funs = tolower) %>%
mutate(year = time)
ggplot() +
geom_line(data = calanus %>% filter(epu == 'GB',
var == 'adt-Spring'),
aes(x = year , y = value, col = epu), lwd = 1) +
geom_line(data = calanus %>% filter(epu == 'MAB',
var == 'adt-Spring'),
aes(x = year , y = value, col = epu), lwd = 1) +
labs(color = c('EPU')) +
theme_minimal()
Georges Bank
# GB
c5.gb <- calanus %>% filter(epu == 'GB', var == 'c5-Spring')
adult.gb <- calanus %>% filter(epu == 'GB', var == 'adt-Spring' )
df.c5 <- dplyr::full_join(recruit, c5.gb, by = join_by(year)) %>%
dplyr::select(year, recruit_est, value) %>%
tidyr::drop_na()
df.adt <- dplyr::full_join(recruit, adult.gb, by = join_by(year)) %>%
dplyr::select(year, recruit_est, value) %>%
tidyr::drop_na()
# Regression
ggscatter(df.c5, x = 'recruit_est', y = 'value',
add = "reg.line", conf.int = TRUE,
cor.coef = TRUE, cor.method = "pearson",
xlab = "Recruitment estimate",
ylab = "Calanus c5 spring (No. per 100m^-3)",
title = 'c5')
ggscatter(df.adt, x = 'recruit_est', y = 'value',
add = "reg.line", conf.int = TRUE,
cor.coef = TRUE, cor.method = "pearson",
xlab = "Recruitment estimate",
ylab = "Calanus adult spring (No. per 100m^-3)",
title = 'Adult')
# GLM
eqn <- as.formula(paste('recruit_est ~', paste(colnames(df.c5)[1],
collapse = " + ")))
mod0 <- glm(recruit_est ~ 1,
data = df.c5,
family = "poisson")
mod1 <- glm(eqn,
data = df.c5,
family = "poisson")
summary(mod0)
##
## Call:
## glm(formula = recruit_est ~ 1, family = "poisson", data = df.c5)
##
## Coefficients:
## Estimate Std. Error z value Pr(>|z|)
## (Intercept) 14.1979354 0.0001802 78775 <0.0000000000000002 ***
## ---
## Signif. codes: 0 '***' 0.001 '**' 0.01 '*' 0.05 '.' 0.1 ' ' 1
##
## (Dispersion parameter for poisson family taken to be 1)
##
## Null deviance: 8933474 on 20 degrees of freedom
## Residual deviance: 8933474 on 20 degrees of freedom
## AIC: 8933809
##
## Number of Fisher Scoring iterations: 4
summary(mod1)
##
## Call:
## glm(formula = eqn, family = "poisson", data = df.c5)
##
## Coefficients:
## Estimate Std. Error z value Pr(>|z|)
## (Intercept) 43.50429247 0.05804867 749.4 <0.0000000000000002 ***
## year -0.01459584 0.00002891 -504.8 <0.0000000000000002 ***
## ---
## Signif. codes: 0 '***' 0.001 '**' 0.01 '*' 0.05 '.' 0.1 ' ' 1
##
## (Dispersion parameter for poisson family taken to be 1)
##
## Null deviance: 8933474 on 20 degrees of freedom
## Residual deviance: 8677368 on 19 degrees of freedom
## AIC: 8677705
##
## Number of Fisher Scoring iterations: 4
AIC(mod0, mod1) %>% dplyr::arrange(AIC)
## df AIC
## mod1 2 8677705
## mod0 1 8933809
null_prediction <- exp(predict(mod0))
mod_prediction <- exp(predict(mod1))
plot(df.c5$year, df.c5$recruit_est, type = 'l')
lines(df.c5$year, null_prediction, col = "gray")
lines(df.c5$year, mod_prediction, col = "red")
Mid-atlantic
# Mid-Atlantic Bight
c5.mab <- calanus %>% filter(epu == 'MAB', var == 'c5-Spring')
adult.mab <- calanus %>% filter(epu == 'MAB', var == 'adt-Spring' )
df.c5 <- dplyr::full_join(recruit, c5.mab, by = join_by(year)) %>%
dplyr::select(year, recruit_est, value) %>%
tidyr::drop_na()
df.adt <- dplyr::full_join(recruit, adult.mab, by = join_by(year)) %>%
dplyr::select(year, recruit_est, value) %>%
tidyr::drop_na()
# Regression
ggscatter(df.c5, x = 'recruit_est', y = 'value',
add = "reg.line", conf.int = TRUE,
cor.coef = TRUE, cor.method = "pearson",
xlab = "Recruitment estimate",
ylab = "Calanus c5 spring (No. per 100m^-3)",
title = 'c5')
ggscatter(df.adt, x = 'recruit_est', y = 'value',
add = "reg.line", conf.int = TRUE,
cor.coef = TRUE, cor.method = "pearson",
xlab = "Recruitment estimate",
ylab = "Calanus adult spring (No. per 100m^-3)",
title = 'Adult')
# microplankton
# Microplankton
# CHL-A
# CHL-A
# CHL-A
# SST fronts
References:
Joyce, Terrence M, Young-Oh Kwon, Hyodae Seo, and Caroline C Ummenhofer. 2019. “Meridional Gulf Stream Shifts Can Influence Wintertime Variability in the North Atlantic Storm Track and Greenland Blocking.” Geophysical Research Letters 46 (3): 1702–8. https://doi.org/10.1029/2018GL081087.
Hobbs, L., Banas, N. S., Cottier, F. R., Berge, J., & Daase, M. (2020). Eat or sleep: availability of winter prey explains mid-winter and spring activity in an Arctic Calanus population. Frontiers in Marine Science, 7, 541564.
Pérez-Hernández, M. Dolores, and Terrence M. Joyce. 2014. “Two Modes of Gulf Stream Variability Revealed in the Last Two Decades of Satellite Altimeter Data.” Journal of Physical Oceanography 44 (1): 149–63. https://doi.org/10.1175/JPO-D-13-0136.1.